CN111821967B - Heterojunction titanium dioxide composite photocatalyst and preparation method thereof - Google Patents
Heterojunction titanium dioxide composite photocatalyst and preparation method thereof Download PDFInfo
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- CN111821967B CN111821967B CN202010729364.9A CN202010729364A CN111821967B CN 111821967 B CN111821967 B CN 111821967B CN 202010729364 A CN202010729364 A CN 202010729364A CN 111821967 B CN111821967 B CN 111821967B
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- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 title claims abstract description 264
- 239000004408 titanium dioxide Substances 0.000 title claims abstract description 127
- 239000011941 photocatalyst Substances 0.000 title claims abstract description 105
- 238000002360 preparation method Methods 0.000 title claims abstract description 28
- 239000002131 composite material Substances 0.000 title claims abstract description 26
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 claims abstract description 103
- 239000013078 crystal Substances 0.000 claims abstract description 7
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 claims description 42
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- 238000001354 calcination Methods 0.000 claims description 36
- 238000000034 method Methods 0.000 claims description 36
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- 238000006243 chemical reaction Methods 0.000 claims description 14
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- UFMBOFGKHIXOTA-UHFFFAOYSA-N 2-methylterephthalic acid Chemical compound CC1=CC(C(O)=O)=CC=C1C(O)=O UFMBOFGKHIXOTA-UHFFFAOYSA-N 0.000 description 1
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J21/00—Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
- B01J21/06—Silicon, titanium, zirconium or hafnium; Oxides or hydroxides thereof
- B01J21/063—Titanium; Oxides or hydroxides thereof
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/30—Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
- B01J35/39—Photocatalytic properties
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/40—Catalysts, in general, characterised by their form or physical properties characterised by dimensions, e.g. grain size
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/38—Organic compounds containing nitrogen
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/10—Photocatalysts
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Abstract
The invention discloses a heterojunction titanium dioxide optical composite catalyst and a preparation method thereof, belonging to the technical field of photocatalysis. The heterojunction titanium dioxide composite photocatalyst is titanium dioxide with a carbon-doped heterojunction structure formed after a titanium metal organic framework is calcined; the titanium dioxide of the heterojunction structure has an anatase crystal form and a rutile crystal form simultaneously. The heterojunction titanium dioxide optical composite catalyst has good adsorption performance and high pollutant photocatalytic degradation efficiency.
Description
Technical Field
The invention belongs to the technical field of photocatalysis, and particularly relates to a heterojunction titanium dioxide optical composite catalyst and a preparation method thereof.
Background
In recent years, due to the increasing emphasis on energy crisis and environmental pollution, the use of photocatalysts to degrade environmental pollutants has received much attention as an environmentally friendly and low-cost technology. A commonly used photocatalyst at present is titanium dioxide. Although titanium dioxide has the advantages of being non-toxic, efficient and inexpensive, its wide forbidden band width results in its absorption of only about 4% of the ultraviolet light in sunlight, which greatly limits its application. Therefore, it is important to develop a photocatalyst or its composite material which can perform catalysis under visible light, and has low cost and stable performance.
Titanium dioxide (TiO) 2 ) Is a photocatalytic material with visible light response, and has attracted people's attention since its emergence. Since carbon nitride has excellent chemical stability and a unique electronic band structure, and also has the advantages of non-toxicity, no metal component and response to visible light, it is widely used in photocatalytic processes such as photocatalytic water splitting, selective photo-organic synthesis, and elimination of organic pollutants in air or water. However, pure phase titanium dioxide has an energy gap of about 3.2eV, and only Taiwan below 360nm can be usedSunlight, and the product is dense block particles, so that the problems of low specific surface area, weak separation capability of photon-generated carriers, poor photocatalytic activity and the like exist, and the application range of the material is limited. At present, titanium dioxide of a derivative heterojunction is obtained by methods such as titanium metal organic framework calcination and the like, so that the photocatalytic performance of the titanium dioxide is improved. The Metal Organic Framework (MOF) derivative material can realize uniform, controllable and uniform doping to a certain extent, so that the MOF derivative material has more excellent performance than the similar inorganic material. The recent reports of MOF derivatization to carbon nanotubes, graphene, and single atom catalyst materials have led to increased interest in MOF derived materials. Among them, element doping in the calcination process is also an important method for practically designing a titanium dioxide-based photocatalytic material with high quantum efficiency, and has great significance for expanding the application range of the titanium dioxide material.
Thus, the invention patent application 202010071814X provides a method for preparing a carbon-doped titanium dioxide photocatalyst, which comprises the steps of: step 1: dissolving an organic ligand and a titanium source in an organic solvent, and heating to obtain a titanium-based metal organic framework material; step 2: and calcining the titanium-based metal organic framework material to obtain the carbon-doped titanium dioxide photocatalyst. The organic ligand is terephthalic acid, 2, 5-dihydroxyterephthalic acid or 2-methyl terephthalic acid.
However, the prior art has the problems that the carbon doping content is not controllable, the derived titanium dioxide is pure phase, and the synthesized carbon-doped titanium dioxide is in a form that the titanium dioxide is coated by a carbon-based material, so that the catalytic range is limited, and the catalytic repair activity of antibiotics is not provided.
Disclosure of Invention
The invention aims to overcome the defects of the prior art, combines a method for constructing heterojunction through derivation and element doping, provides a titanium metal organic framework (Ti-MOF) derivative photocatalyst which is green, environment-friendly, high in visible light absorption capacity, high in photo-generated charge separation rate, high in photocatalytic activity, stable in chemical property and corrosion-resistant, and further provides a one-step preparation method of the titanium metal organic framework (Ti-MOF) derivative photocatalyst which is simple in preparation process, easy to control, easy in raw material obtaining, low in cost and suitable for continuous large-scale batch production.
In order to solve the technical problems, the technical scheme adopted by the invention is as follows:
a heterojunction titanium dioxide composite photocatalyst is characterized in that the heterojunction titanium dioxide composite photocatalyst is titanium dioxide of a carbon-doped heterojunction structure formed after a titanium metal organic framework is calcined; the titanium dioxide of the heterojunction structure has an anatase crystal form and a rutile crystal form simultaneously.
The material synthesized by the prior art is a material of carbon-based material coated with nano titanium dioxide, and NH is used for the invention 2 MIL-125 as a template, and the carbon element uniformly doped in the titanium dioxide material is obtained by calcination, as can be seen from mapping chart (FIG. 5) and C spectrum (FIG. 3 b) in XPS chart. In addition, the titanium dioxide obtained by calcination is titanium dioxide with a heterojunction structure, and an XRD (figure 1) shows that the titanium dioxide with the heterojunction structure simultaneously has two crystal forms of anatase and rutile, and the combination of the titanium dioxide with the heterojunction structure and nonmetal doping has a good synergistic effect in the aspect of photocatalytic degradation, which is extremely rare in the field and is the core innovation of the invention. It is known in the art that the difference of the morphology of the photocatalytic material can lead to different photocatalytic applications and catalytic activities, and any change in the structure and morphology of the photocatalyst can affect the catalytic function and catalytic activity of the photocatalyst. The greatest contribution of the present invention compared to the prior art is the accidental discovery of calcined NH 2 MIL-125 (Ti) can derive titanium dioxide with a special structure and has excellent antibiotic catalytic repair activity, and titanium dioxide with a heterojunction structure has stronger capability of separating photogenerated electrons from holes, which cannot be realized by the prior art.
The titanium dioxide of the carbon-doped heterojunction structure is of a round cake-shaped structure, and carbon elements are uniformly doped in the titanium dioxide;
preferably, the diameter of the discoid structure is 150-250nm, preferably 200nm.
The weight ratio of carbon to titanium dioxide in the carbon-doped titanium dioxide is 22-45: 55-78, preferably 25.82: 74.18.
The titanium metal organic framework is NH 2 -MIL-125 type titanium metal organic framework.
A preparation method of a heterojunction titanium dioxide composite photocatalyst is characterized in that a titanium metal organic framework is calcined.
The calcination refers to placing the titanium metal organic framework in a muffle furnace for calcination for 1-10h, preferably 5h; the calcination temperature is 300-600 ℃, preferably 400 ℃; the heating rate is 3-13 deg.C/min, preferably 5 deg.C/min.
The titanium metal organic framework is NH 2 -MIL-125 type titanium metal organic framework.
With this type of MOF material, a high density of immobilized Ti sites can be introduced in the porous MOF, and the derived product is easily obtained by means of calcination or the like. There are no other types of photocatalysts that can be derived from titanium dioxide that have been reported in the art, and there are more than 20 in a large category of titanium metal organic frameworks, e.g., MIL-125, NH 2 -MIL-125、PCN-415、NH 2 PCN-415, NTU-9, etc., which are synthesized by changing the titanium source or ligand. Although the prior art synthesized titanium metal organic framework is not explicitly described, it can be seen from the type of ligand that MIL-125 is synthesized, while NH is synthesized in the present invention 2 The amino group of MIL-125 type is a substance which is remarkably different from the amino group of MIL-125 type, and a substance with different structure and appearance is generated after calcination, so that the application range, the catalytic object and the catalytic effect of the amino group are far from each other.
NH 2 Although commercially available, the commercial production of the titanium metal organic framework type-MIL-125 is not possible in principle for the preparation of the catalyst of the invention by calcination and for the degradation of antibiotics, because of its high cost, and therefore NH can be prepared economically in large quantities by the above-mentioned preparation method of the invention 2 the-MIL-125 type titanium metal organic framework is widely applied to the field of antibiotic degradation and restoration after being calcined. Meanwhile, the preparation method of the invention can realize final carbon doping by adjusting different calcination temperaturesThe carbon doping content of the titanium dioxide composite photocatalyst with the heterojunction structure is controllable, the higher the temperature is within the range of 200-400 ℃, the lower the carbon doping content is, the better the catalytic activity is, but within the range of 400-600 ℃, the higher the temperature is, the lower the carbon doping content is, and the catalytic activity is reduced.
The titanium metal organic framework is prepared by the following steps:
(1) Dissolving 2-amino-terephthalic acid in N, N-dimethylformamide and anhydrous methanol to obtain a mixture solution,
(2) Quickly adding tetrabutyl titanate into the mixture solution, uniformly mixing, and reacting at high temperature;
preferably, the blending refers to stirring for 30min; the reaction at high temperature means that the reaction is carried out in an oven at 150 ℃ for 24 hours.
After the reaction at high temperature, washing the obtained product with N, N-dimethylformamide and anhydrous methanol for three times respectively, and drying;
preferably, the drying refers to drying for 12 hours in a vacuum environment at 80 ℃.
The dosage proportion of the 2-amino-terephthalic acid, the N, N-dimethylformamide, the anhydrous methanol and the tetrabutyl titanate is 0.8-1.2 g: 20-30 ml: 2-5 ml: 0.1-1ml, and the optimal proportion is 1.087 g: 25 ml: 2.7 ml: 0.52ml.
A carbon-doped titanium dioxide photocatalyst derived from titanium metal organic framework and a preparation method thereof, wherein the photocatalyst is NH 2 the-MIL-125 type titanium metal organic framework is used as a template and is prepared by a calcining method in one step.
A carbon-doped titanium dioxide catalyst derived from a titanium metal organic framework, comprising the steps of: mixing 2-amino-terephthalic acid, absolute methanol and N, N-dimethylformamide, adding tetrabutyl titanate, and stirring to obtain a titanium metal organic framework; and calcining the titanium metal organic framework to obtain the carbon-doped titanium dioxide photocatalyst.
In the above-mentioned titanium metal organic skeleton derivative photocatalyst, it is preferable that the molar ratio of the 2-amino-terephthalic acid to tetra-N-butyl titanate is 25% and the volume ratio of the solvent anhydrous methanol N, N-dimethylformamide is 10 to 15%.
In the above titanium metal organic framework derivative photocatalyst, preferably, the temperature increase rate during the calcination process is 5 ℃/min.
In the above titanium metal organic framework derivative photocatalyst, preferably, the calcination temperature is 400 ℃; the calcination time was 5h.
In the above titanium metal organic framework derivative photocatalyst, preferably, the mixing method is to put 2-amino-terephthalic acid and tetra-N-butyl titanate and solvent anhydrous methanol N, N-dimethylformamide into a reaction kettle at 150 ℃ for 24 hours to obtain NH 2 -MIL-125 type titanium metal organic framework.
As a general technical concept, the invention also provides a preparation method of the titanium metal organic framework derivative photocatalyst, which comprises the following steps: dissolving 2-amino-terephthalic acid in anhydrous methanol and N, N-dimethylformamide, adding tetrabutyl titanate, stirring, placing in a reaction kettle at 150 deg.C for 24 hr to obtain NH 2 -MIL-125 type titanium metal organic framework (derivative precursor); and calcining the derivative precursor to obtain the carbon-doped titanium dioxide photocatalyst.
In the above production method, it is preferable that the molar ratio of the 2-amino-terephthalic acid to tetra-N-butyl titanate is 25% and the volume ratio of the solvent anhydrous methanol N, N-dimethylformamide is 10 to 15%.
In the above preparation method, preferably, the temperature increase rate during the calcination is 5 ℃/min.
In the preparation method, the calcination temperature is preferably 300-600 ℃; the calcination time was 5h.
In the above preparation method, preferably, the mixing method is to dissolve 2-amino-terephthalic acid in anhydrous methanol and N, N-dimethylformamide, add tetrabutyl titanate and stir for 20min to 30min, so as to obtain the titanium metal organic framework precursor.
The invention discloses a carbon-doped titanium dioxide derived from a titanium metal organic frameworkTitanium oxide photocatalyst and preparation method thereof, wherein the photocatalyst is NH 2 the-MIL-125 type titanium metal organic framework is used as a template and is prepared by a calcining method in one step. The carbon-doped titanium dioxide photocatalyst has the advantages of environmental protection, strong visible light absorption capacity, high photoproduction charge separation rate, high photocatalytic activity, stable chemical property, corrosion resistance and the like, and the preparation method has the advantages of simplicity, easiness in operation and control, easiness in obtaining of raw materials, low cost, suitability for continuous large-scale batch production and the like.
Compared with the prior art, the invention has the advantages that:
1. the invention provides a titanium metal organic framework derivative photocatalyst which is prepared from NH 2 the-MIL-125 type titanium metal organic framework is a template of the derivative, and the titanium metal organic framework is derived into carbon-doped titanium dioxide by calcining in the air atmosphere, so that the carbon-doped titanium dioxide photocatalyst has stronger visible light absorption capacity and higher electron-hole separation efficiency, the effect of comprehensively improving is achieved, and the problems of insufficient visible light absorption capacity, high photogenerated electron-hole pair recombination rate and the like of a titanium dioxide monomer are effectively solved. Compared with a pure titanium metal organic framework, the titanium metal organic framework derivative photocatalyst of the invention has more excellent photocatalytic activity.
2. The titanium metal organic framework derivative photocatalyst has small influence of self toxicity on the environment, is green and environment-friendly, is easy to be practically applied, and has good environmental protection benefit.
3. The invention also provides a preparation method of the titanium metal organic framework derivative photocatalyst, which takes copper chloride dihydrate as a copper source and NH 2 the-MIL-125 type titanium metal organic framework is used as a template, and the photocatalyst is prepared by one step through a calcination method. In the present invention, NH 2 The MIL-125 type titanium metal organic framework is subjected to structural collapse and is converted into heterojunction titanium dioxide, and part of carbon is doped into the titanium dioxide structure in an ion form, so that a stable carbon-doped titanium dioxide photocatalyst is formed.
4. The preparation method adopts a one-step calcining method, has the advantages of simple preparation process, easy control, easily obtained raw materials, low cost, low energy consumption, short time consumption and the like, is suitable for continuous large-scale batch production, and is convenient for industrial utilization.
The photocatalyst provided by the prior art is used for degrading dyes and phenolic substances, while the photocatalyst provided by the invention is used for degrading tetracycline hydrochloride, and because the adopted preparation raw materials are different, the synthesized titanium metal organic frameworks are different, and further, the photocatalyst is a derivative product obtained by calcining based on different titanium metal organic frameworks: the difference of the material structure of the photocatalyst leads to the difference of the photocatalysis principle, so that the catalytic reaction objects of the photocatalyst and the photocatalyst are greatly different. The invention is through the reaction of NH 2 -MIL-125 titanium organometallic framework by calcination, with a reduction in TiO due to the uniform doping of the titanium dioxide with carbon 2 The band gap of the light guide plate improves the absorption range of visible light in sunlight. Under the irradiation of light, a large number of holes and superoxide radicals are generated by the catalyst, and the two active substances attack antibiotics, so that the groups of the antibiotics are destroyed and further converted into organic small molecules, and the organic small molecules are mineralized into substances such as titanium dioxide, water and the like. The generation of a large number of cavities by the photocatalyst under light conditions is a key factor in the photodegradation process herein. Meanwhile, the material disclosed by the invention can be well applied to an actual water body, and a plurality of actual influence factors are made subsequently. The degradation effect of the medical wastewater on antibiotics shows that the photocatalytic material has strong practical application capability.
Drawings
FIG. 1 shows T-300, T-400, T-500, T-600 in examples 1 to 4 of the present invention and NH in comparative example 1 2 -XRD diffraction pattern of MIL-125.
FIG. 2 shows NH in T-300, T-400, T-500, T-600 in examples 1 to 4 of the present invention and in comparative example 1 2 FTIR diffraction pattern of MIL-125.
FIG. 3 is XPS survey spectra (a) and (b) C1s spectra of T-400 of the titanium metal organic framework and the photocatalyst derived therefrom (T-400) obtained in example 1 of the present invention.
FIG. 4 is an SEM photograph of the titanium metal organic framework (left drawing) and the photocatalyst (T-400) derived therefrom (right drawing) obtained in example 1 of the present invention.
FIG. 5 is an EDX profile (Mapping chart) of the titanium metal organic framework derivative photocatalyst (T-400) prepared in example 1 of the present invention.
FIG. 6 shows T-300, T-400, T-500, T-600, NH in this example 1 2 Graph of photocatalytic degradation of MIL-125 material to tetracycline hydrochloride.
FIG. 7 is a graph of the photocatalytic removal rate of tetracycline hydrochloride at different pH values of the carbon-doped titanium dioxide material (T-400) of the titanium metal organic framework derivative in this example 2.
Fig. 8 is a graph of the photocatalytic removal rate of tetracycline hydrochloride from the carbon-doped titanium dioxide material (T-400) of the titanium metal organic framework derivative in this example 3 under the influence of different ions. FIG. 8 shows the effect of cationic ion on the left and the effect of anionic ion on the right.
FIG. 9 is a graph of the photocatalytic removal rate of tetracycline hydrochloride from the carbon-doped titanium dioxide material (T-400) of the titanium metal organic framework derivative of this example 4 under the influence of different nutrient source factors. FIG. 9 shows phosphate (NaH) on the left 2 PO 4 ) The influence effect diagram is shown on the right, and the influence effect diagram of organic matters (HA) is shown on the right.
Fig. 10 is a graph of the photocatalytic degradation effect of the titanium dioxide material (T-400) doped with carbon and serving as the titanium metal organic framework derivative in the embodiment 5 on tetracycline hydrochloride in different practical water bodies.
Detailed Description
In order to make the objects, technical solutions and advantages of the embodiments of the present invention clearer, the technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the drawings in the embodiments of the present invention. The invention is further described below with reference to the drawings and specific preferred embodiments of the description, without thereby limiting the scope of protection of the invention.
The materials and equipment used in the following examples are commercially available.
Comparative example 1:
NH (hydrogen sulfide) 2 The preparation method of the-MIL-125 type titanium metal organic framework comprises the following steps:
(1) 1.087g of 2-amino-terephthalic acid was weighed out and dissolved completely in N, N-dimethylformamide (25 mL) and dry methanol (2.7 mL).
(2) 0.52mL of tetrabutyl titanate was quickly added to the mixture solution obtained in step (1), and the mixture was stirred for 30min.
(3) And (3) placing the mixture solution obtained in the step (2) into a reaction kettle, placing the reaction kettle into an oven for reacting for 24 hours, and controlling the temperature of the oven to be 150 ℃.
(4) Respectively washing the product obtained in the step (3) with N, N-dimethylformamide and anhydrous methanol for three times, and drying at 80 ℃ for 12 hours in a vacuum environment to obtain the titanium metal organic framework photocatalyst named as NH 2 -MIL-125。
Example 1:
the invention relates to a carbon-doped titanium dioxide photocatalyst derived from a titanium metal organic framework and a preparation method thereof, wherein the photocatalyst is NH 2 the-MIL-125 type titanium metal organic framework is used as a template and is prepared by a calcining method in one step.
The preparation method of the carbon-doped titanium dioxide photocatalyst derived from the titanium metal organic framework in the embodiment includes the following steps:
(1) 1.087g of 2-amino-terephthalic acid was weighed and dissolved completely in N, N-dimethylformamide (25 mL) and dry methanol (2.7 mL).
(2) 0.52mL of tetra-n-butyl titanate was quickly added to the mixture solution obtained in step (1), and the mixture was stirred for 30min.
(3) And (3) placing the mixture solution obtained in the step (2) into a reaction kettle, placing the reaction kettle into an oven for reacting for 24 hours, and controlling the temperature of the oven to be 150 ℃.
(4) Respectively washing the product obtained in the step (3) with N, N-dimethylformamide and anhydrous methanol for three times, and drying at 80 ℃ for 12 hours in a vacuum environment to obtain the titanium metal organic framework photocatalyst named as NH 2 -MIL-125。
(5) And (3) placing the titanium metal organic framework obtained after uniform grinding in the step (4) into a crucible, placing the crucible into a muffle furnace for calcining, controlling the heating rate of the muffle furnace to be 5 ℃/min, keeping the temperature at 300 ℃ for 5h, and cooling and grinding a calcined product to obtain the carbon-doped titanium dioxide photocatalyst of the titanium metal organic framework derivative, which is named as T-300.
Example 2:
a method for preparing a titanium dioxide photocatalyst doped with carbon, which is a titanium metal organic framework derivative, of the present invention is substantially the same as the preparation method in example 1 except that: the temperature of the muffle furnace in the step (5) is 400 ℃. The titanium metal organic framework derivative carbon doped titanium dioxide photocatalyst prepared in example 2 was named T-400.
Example 3:
a method for preparing a titanium dioxide photocatalyst doped with carbon, which is a titanium metal organic framework derivative, of the present invention is substantially the same as the preparation method in example 1 except that: the temperature of the muffle furnace in the step (5) is 500 ℃. The titanium metal organic framework derivative carbon doped titanium dioxide photocatalyst prepared in example 2 was named T-500.
Example 4:
a method for preparing a titanium dioxide photocatalyst doped with carbon, which is a titanium metal organic framework derivative, of the present invention is substantially the same as the preparation method in example 1 except that: the temperature of the muffle furnace in the step (5) is 600 ℃. The carbon-doped titanium dioxide photocatalyst of the titanium metal organic framework derivative prepared in example 2 was named T-600.
T-300, T-400, T-500, T-600 in examples 1 to 4, and NH in comparative example 1 2 XRD analysis of MIL-125 gave the results shown in FIG. 1. FIG. 1 shows T-300, T-400, T-500, T-600 in examples 1 to 4 of the present invention and NH in comparative example 1 2 -XRD diffraction pattern of MIL-125. As shown in FIG. 1, the XRD pattern results of example 1 revealed that T-300 derived from a titanium metal organic skeleton was not completely converted. Examples 2 to 4 each contain the characteristic peaks (101) and (110) of titanium dioxide, which indicates that the majority of all samples were titanium dioxide and that the conversion from the titanium metal organic framework to titanium dioxide has been successfully completed. And the structure is a heterojunction structure of anatase and rutile, so that the separation efficiency of photo-generated electrons and holes can be improved. FIG. 2 shows T-300, T-400, and,NH in T-500, T-600, and comparative example 1 2 FTIR spectrum of MIL-125. As shown in FIG. 2, the IR peaks in example 1 and comparative example 1 are substantially identical, indicating that T-300 derived from a titanium metal organic framework has not been completely converted. The embodiment cases 2 to 4 are all 500 to 1000cm -1 The characteristic peak of titanium dioxide appears at the position of (a), and the characteristic peak of the titanium metal organic framework can not be observed in an infrared image, which indicates that the main body of all samples is titanium dioxide, the titanium metal organic framework is completely converted into titanium dioxide after being calcined, and the process of converting the titanium metal organic framework into the titanium dioxide is successfully completed. FIG. 3 (a) is an XPS survey of the titanium metal organic framework derivative photocatalyst prepared in examples 1 to 4 of the present invention and comparative example 1. As can be seen from FIG. 3, example 1 and comparative example 1 have four elements of C, N, O and Ti, while the examples 2 to 4 have no element of N. Fig. 3 (b) is an XPS spectrum of the titanium metal organic framework derivative photocatalyst prepared in example 2 of the present invention, and binding energies of 288.69 and 286.19eV appear in the C2 p electron orbital energy spectrum, which is a typical feature of C element doping, indicating that C is present in titanium dioxide.
SEM analysis was performed on the titanium dioxide photocatalyst (T-400) doped with carbon, which is a titanium metal organic skeleton derivative prepared in example 2 of the present invention. FIGS. 4a, b are SEM images of carbon-doped titanium dioxide photocatalyst (T-400) of a titanium metal organic framework derivative prepared in example 2 of the present invention. From the left panel, it can be seen that NH 2 MIL-125 has a typical discoid morphology, in regular blocks. FIG. 4c, d is an SEM image of a carbon-doped titanium dioxide photocatalyst (T-400) of a titanium metal organic framework derivative prepared in example 2 of the present invention. As can be seen from the right, T-400 has a discoid structure with NH 2 The morphological features of MIL-125 are similar, the size is significantly reduced, and the surface of the derivative is rougher. By analyzing with the combination of fig. 1, fig. 2, fig. 3 and fig. 4, the invention successfully synthesizes the composite photocatalyst of the carbon-doped titanium dioxide derived from the titanium metal organic framework.
FIG. 6 shows NH in T-300, T-400, T-500, T-600 in example 1 and in comparative example 1 2 -MIL-125 para-tetracycline hydrochlorideWherein the initial concentration is the concentration of tetracycline hydrochloride at which adsorption equilibrium is reached. As can be seen from FIG. 5, NH in T-300, T-400, T-500, T-600 of the present invention and comparative example 1 2 The photodegradation rates of the MIL-125 to the tetracycline hydrochloride after 1 hour of illumination are respectively 21.3%, 85.1%, 81.1%, 58.2% and 19.3%. Therefore, the carbon-doped titanium dioxide material derived from the titanium metal organic framework has greatly enhanced photocatalytic effect on tetracycline hydrochloride, and the photocatalytic effect is the best when the calcining temperature is 400 ℃. Notably, compared to titanium metal organic frameworks (NH) 2 MIL-125), and the carbon-doped titanium dioxide material derived from the material greatly promotes the separation of photon-generated carriers and greatly improves the photocatalytic effect of the material.
Example 5
A method for preparing a carbon-doped titanium dioxide photocatalyst (T-400) derived from a titanium metal organic framework is used for photocatalytic degradation of tetracycline hydrochloride in a water body, and comprises the following steps:
6 parts of the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework prepared in example 1 were weighed and added, 30mg each, to 5 parts of 100mL of 10mg/L tetracycline hydrochloride solution at pH values of 2,3,4,5,6,7, respectively. And (2) uniformly mixing and dispersing the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework in a tetracycline hydrochloride solution, and magnetically stirring for 1h at the rotating speed of 420r/min to finish the adsorption balance treatment on the antibiotic solution.
Then, a light source is turned on, and the light is irradiated under visible light (lambda is more than or equal to 420 nm) to carry out photocatalytic reaction for 1h. In the process of illumination, stirring and illumination, taking 4mL of sample every 10min, centrifuging the sample, measuring the absorbance of the centrifuged supernatant through an ultraviolet-visible spectrophotometer, and determining the concentration of the illuminated antibiotic, thereby obtaining the photocatalytic degradation effect of the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework on tetracycline hydrochloride. Fig. 7 is a graph showing the effect of carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework in example 2 on the photocatalytic degradation of tetracycline hydrochloride at different pH values. As can be seen from FIG. 7, when the pH values of the tetracycline hydrochloride solution were 2,3,4,5,6,7, respectively, the removal rates of the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework to tetracycline hydrochloride were 32.7%, 81.6%, 94.2%, 85.1%, 86.3%, and 89.5%, respectively. The pH affects the charge of the material and the morphology of the tetracycline hydrochloride molecule. Different pH values can enable the tetracycline hydrochloride to have different surface charge properties according to the zeta potential of the T-400, thereby influencing the mutual adsorption of the tetracycline hydrochloride and the T-400 surface. With the increase of the pH value, the photocatalytic degradation rate of the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework prepared by the method for preparing the tetracycline hydrochloride antibiotic is increased. Particularly, the carbon-doped titanium dioxide photocatalyst (T-400) of the derivative prepared by the invention has the best effect on removing tetracycline hydrochloride antibiotics at the pH value of 4.
Example 6
A method for preparing a carbon-doped titanium dioxide photocatalyst (T-400) derived from a titanium metal organic framework is used for photocatalytic degradation of tetracycline hydrochloride in a water body, and comprises the following steps:
8 parts of carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework prepared in example 1 are weighed, 30mg of the photocatalyst is added into 8 parts of 100mL 10mg/L aureomycin hydrochloride solution respectively, the mixture is uniformly mixed and dispersed, and cations in the solution are 10mmol/L Na in turn + 、K + 、Zn 2+ 、Mg 2+ The anions in the solution are 10mmol/L Cl in sequence - 、NO 2 - 、NO 3 - 、SO 4 2- . Magnetically stirring for 1h at the rotating speed of 420r/min to complete the adsorption balance treatment of the antibiotic solution.
Then, a light source is turned on, and the light is irradiated under visible light (lambda is more than or equal to 420 nm) to carry out photocatalytic reaction for 1h. In the illumination stirring process, taking 4mL of sample every 10min, centrifuging the sample, measuring the absorbance of the supernatant obtained after centrifugation by using an ultraviolet-visible spectrophotometer, and determining the concentration of the antibiotic after illumination, thereby obtaining the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework for photocatalytic degradation of tetracycline hydrochlorideAnd (5) effect. Fig. 9 is a graph showing the photocatalytic degradation effect of the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework on tetracycline hydrochloride under the influence of different ions in example 3. FIG. 9 shows the effect of cation on the left and the effect of anion on the right. As can be seen from FIG. 8, the cations in the tetracycline hydrochloride solution were Na, respectively + 、K + 、Zn 2+ 、Mg 2+ In the case of the titanium metal organic framework derivative, the removal rates of the carbon-doped titanium dioxide photocatalyst (T-400) on tetracycline hydrochloride are 75.6%, 78.5%, 80.6% and 73.3%, respectively. Anions are respectively Cl - 、NO 3 - 、SO 4 2- 、CO 3 2- When the catalyst is used, the removal rates of the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework to chlortetracycline hydrochloride are respectively 75.6%, 76.6%, 70.1% and 15.1%. These results demonstrate that the effect of different ionic species on the photocatalytic removal process is different, as additional oxidizing species may be generated, thereby affecting the efficiency of photocatalytic degradation of tetracycline.
Example 7
A method for preparing a carbon-doped titanium dioxide photocatalyst (T-400) derived from a titanium metal organic framework is used for photocatalytic degradation of tetracycline hydrochloride in a water body, and comprises the following steps:
6 parts of carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework prepared in example 1 are weighed, 30mg of the photocatalyst is added into 6 parts of 100mL 10mg/L chlortetracycline hydrochloride solution respectively, the mixture is uniformly mixed and dispersed, and the nutrient source influence factors in the solution are 5mg/L NaH in turn 2 PO 4 、10mg/L NaH 2 PO 4 、20mg/L NaH 2 PO 4 (ii) a 5mg/L HA, 10mg/L HA, 20mg/L HA. Magnetically stirring for 2h at the rotating speed of 420r/min to complete the adsorption balance treatment of the antibiotic solution.
Then, a light source is turned on, and the light is irradiated under visible light (lambda is more than or equal to 420 nm) to carry out photocatalytic reaction for 1h. Taking 4mL of sample every 10min in the illumination stirring process, centrifuging the sample, and taking supernatant obtained after centrifugation to be visible through ultraviolet lightAnd (3) measuring the absorbance by a spectrophotometer, and determining the concentration of the antibiotic after illumination, thereby obtaining the photocatalytic degradation effect of the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework on the tetracycline hydrochloride. Fig. 9 is a graph showing the effect of carbon-doped titanium dioxide photocatalyst (T-400) derived from a titanium metal organic framework on the photocatalytic degradation of tetracycline hydrochloride under the influence of different nutrient source factors in example 4. FIG. 9 shows phosphate (NaH) on the left 2 PO 4 ) The influence effect diagram is shown on the right, and the organic matter (HA) influence effect diagram is shown on the right.
As can be seen from FIG. 9, in the presence of an appropriate amount of H 2 PO 4 - Under the action of the catalyst, a bridge is formed between TC-HCl and phosphate, and the adsorption of the TC-HCl on the photocatalyst can be promoted. The photocatalytic removal efficiency can be accelerated in the first time (at H) 2 PO 4 - At concentrations of 5mg/L and 10mg/L, the photocatalytic removal rates were 57.5% and 53.39% within 10min, but H 2 PO 4 Competing with TC-HCl molecules for active radicals, eventually leading to a decrease in photocatalytic removal efficiency. 5mg/L NaH 2 PO 4 、10mg/L NaH 2 PO 4 、20mg/L NaH 2 PO 4 The removal rates were 80.3%,74.3% and 69.4%, respectively. At Humic Acid (HA) concentrations of 5mg/L, 10mg/L and 20mg/L, TC-HCl removal rates of 71.8%, 60.2% and 41.4% were observed, and HA (humic acid) may act as a filter and an xOH scavenger, hindering TC-HCl photocatalytic degradation efficiency.
Example 8
A method for preparing a carbon-doped titanium dioxide photocatalyst (T-400) derived from a titanium metal organic framework is used for photocatalytic degradation of tetracycline hydrochloride in a water body, and comprises the following steps:
5 parts of carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework prepared in example 1, 30mg of each part, are respectively added into 4 parts of 100mL of 10mg/L different aureomycin hydrochloride water bodies, and the mixture is uniformly mixed and dispersed, wherein the water body substrates are deionized water, tap water, lake water, hunan river water and medical wastewater in turn. Magnetically stirring for 1h at the rotating speed of 420r/min to complete the adsorption balance treatment of the antibiotic solution.
Then, a light source is turned on, and the light is irradiated under visible light (lambda is more than or equal to 420 nm) to carry out photocatalytic reaction for 1h. In the illumination stirring process, taking 4mL of sample every 10min, centrifuging the sample, measuring the absorbance of the supernatant obtained after centrifugation by using an ultraviolet-visible spectrophotometer, and determining the concentration of the antibiotic after illumination, thereby obtaining the photocatalytic degradation effect of the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework on tetracycline hydrochloride. Fig. 10 is a graph illustrating the effect of carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework in example 5 on the photocatalytic degradation of tetracycline hydrochloride in different water bodies. As can be seen from FIG. 10, the TC-HCl removal rates in ionized water, tap water, lake water, xiangjiang water, and medical wastewater are 85.1%, 66.3%, 71.1%, 70.7%, and 62.7%, respectively. Thus, the removal rate of TC-HCl in a real water matrix is inhibited to a different extent than standard deionized water. Although the removal rate of CTC-HCl in the actual water matrix is reduced compared to deionized water, the total amount of organic carbon removed in the actual water matrix is significantly higher than the total amount of organic carbon removed in the deionized water matrix due to the much higher initial TOC value in the actual water matrix.
Therefore, in the method for removing the antibiotics in the water body by using the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework, the carbon-doped titanium dioxide photocatalyst (T-400) derived from the titanium metal organic framework is mixed with tetracycline hydrochloride wastewater to be stirred and adsorbed, and then photocatalytic degradation is carried out under simulated sunlight, so that the antibiotics in the wastewater can be efficiently adsorbed and photocatalytic degraded.
The above description is only a preferred embodiment of the present invention, and the scope of the present invention is not limited to the above-described examples. All technical schemes belonging to the idea of the invention belong to the protection scope of the invention. It should be noted that modifications and embellishments within the scope of the invention may be made by those skilled in the art without departing from the principle of the invention, and such modifications and embellishments should also be considered as within the scope of the invention.
Claims (13)
1. A heterojunction titanium dioxide composite photocatalyst is characterized in that the heterojunction titanium dioxide composite photocatalyst is titanium dioxide of a carbon-doped heterojunction structure formed after a titanium metal organic framework is calcined; the titanium dioxide of the heterojunction structure has an anatase crystal form and a rutile crystal form simultaneously; the titanium metal organic framework is NH 2 -MIL-125 type titanium metal organic framework, said calcining being a calcining of said titanium metal organic framework in a muffle furnace for 5h; the calcining temperature is 400 ℃; the heating rate was 5 ℃/min.
2. The heterojunction titanium dioxide composite photocatalyst of claim 1, wherein the titanium dioxide of the carbon-doped heterojunction structure is a round cake structure, and carbon element is uniformly doped in the titanium dioxide.
3. The heterojunction titanium dioxide composite photocatalyst as claimed in claim 2, wherein the diameter size of the round cake-shaped structure is 150-250nm.
4. The heterojunction titanium dioxide composite photocatalyst as claimed in claim 3, wherein the diameter of the discoid structure is 200nm.
5. A heterojunction titanium dioxide composite photocatalyst as claimed in any of claims 1 to 4, wherein the weight ratio of carbon to titanium dioxide in the carbon-doped titanium dioxide is 22-45: 55-78.
6. The heterojunction titanium dioxide composite photocatalyst as claimed in claim 5, wherein the weight ratio of carbon to titanium dioxide in the carbon-doped titanium dioxide is 25.82: 74.18.
7. A preparation method of a heterojunction titanium dioxide composite photocatalyst is characterized in that a titanium metal organic framework is calcined; the calcining refers to calcining the titanium metal organic framework in a muffle furnace for 5 hours; the calcining temperature is 400 ℃; the heating rate is 5 ℃/min; the titanium metal organic framework is NH 2 -MIL-125 type titanium metal organic framework.
8. The method for preparing the heterojunction titanium dioxide composite photocatalyst as claimed in claim 7, wherein the titanium metal organic framework is prepared by the following steps:
(1) Dissolving 2-amino-terephthalic acid in N, N-dimethylformamide and anhydrous methanol to obtain a mixture solution,
(2) And quickly adding tetrabutyl titanate into the mixture solution, uniformly mixing, and reacting at high temperature.
9. The method for preparing the heterojunction titanium dioxide composite photocatalyst as claimed in claim 8, wherein the mixing means stirring for 30min; the reaction at high temperature means that the reaction is carried out in an oven at 150 ℃ for 24 hours.
10. The method for preparing the heterojunction titanium dioxide composite photocatalyst as claimed in claim 8, wherein the product obtained after the reaction at the high temperature is dried after being washed with N, N-dimethylformamide and anhydrous methanol three times respectively.
11. The method for preparing the heterojunction titanium dioxide composite photocatalyst as claimed in claim 10, wherein the drying refers to drying at 80 ℃ for 12 hours in a vacuum environment.
12. The method for preparing the heterojunction titanium dioxide composite photocatalyst as claimed in claim 8, wherein the dosage ratio of the 2-amino-terephthalic acid, the N, N-dimethylformamide, the anhydrous methanol and the tetra-N-butyl titanate is 0.8-1.2 g: 20-30 ml: 2-5 ml: 0.1-1ml.
13. The method for preparing the heterojunction titanium dioxide composite photocatalyst as claimed in claim 12, wherein the dosage ratio of the 2-amino-terephthalic acid, the N, N-dimethylformamide, the anhydrous methanol and the tetra-N-butyl titanate is 1.087 g: 25 ml: 2.7 ml: 0.52ml.
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| CN109880114A (en) * | 2019-03-12 | 2019-06-14 | 北京科技大学 | A kind of Ti-MOFs material and preparation method thereof using solvent structure |
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Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108654605A (en) * | 2017-08-05 | 2018-10-16 | 宁波大学 | The preparation method of the porous carbon-based titanium dioxide photochemical catalyst of modified by silver for degradation of phenol |
| CN109880114A (en) * | 2019-03-12 | 2019-06-14 | 北京科技大学 | A kind of Ti-MOFs material and preparation method thereof using solvent structure |
Non-Patent Citations (1)
| Title |
|---|
| Ti-MOF Derived N-Doped TiO2 Nanostructure as Visible-light-driven Photocatalyst;HE Yilei等;《Chem. Res.Chinese Universities》;20200515;第1-6页 * |
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